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混合细菌菌落在水溶液中对铬(Cr)的微生物还原命运。

Microbial reduction fate of chromium (Cr) in aqueous solution by mixed bacterial consortium.

机构信息

School of Water Resources and Environment, MOE Key Laboratory of Groundwater Circulation and Environmental Evolution, China University of Geosciences (Beijing), Beijing 100083, PR China.

School of Sciences, China University of Geosciences (Beijing), Beijing 100083, PR China.

出版信息

Ecotoxicol Environ Saf. 2019 Apr 15;170:763-770. doi: 10.1016/j.ecoenv.2018.12.041. Epub 2018 Dec 21.

Abstract

Groundwater contaminated by Cr(VI) requires effective remediation to prevent adverse environmental impacts. The biodegradation of Cr(VI) has been documented for several decades, but little remains known about the removal fate of chromium, including the main species of reductase (sites) and functional genes involved in Cr(VI) reduction in mixed bacterial consortium. Cr(VI) reduction in this study was verified to be an enzyme-mediated process. Meanwhile, Cr(VI) reduction of different cell components demonstrated that the extracellular enzyme was the main active substance, and the distribution of Cr after experiment was quantified using mass balance calculation. Furthermore, the optimal pH for reduction was 8.0, with the reduction rate decreasing with increasing initial Cr(VI) concentrations. The co-existing oxyanions had little effect on Cr(VI) reduction, while the presence of other heavy metals had a relatively significant influence. The evolutionary behavior of microbial community structure and functional genes affected by Cr(VI) were also analyzed, which provided new insights on the underlying mechanisms involved in bioreduction in this study. These results generated new understanding of the reduction mechanisms on the Cr-relevant bacterial species and genes, which would be helpful in designing strategies for the bioremediation of Cr(VI) contaminated water.

摘要

受六价铬污染的地下水需要进行有效的修复,以防止对环境产生不利影响。几十年来,已经有文献记载了六价铬的生物降解,但对于铬的去除命运,包括混合细菌群落中参与六价铬还原的主要还原酶(部位)和功能基因,人们知之甚少。本研究证实,六价铬的还原是一个酶介导的过程。同时,不同细胞成分的六价铬还原表明,细胞外酶是主要的活性物质,并通过质量平衡计算定量了实验后铬的分布。此外,还原的最佳 pH 值为 8.0,随着初始六价铬浓度的增加,还原速率降低。共存的含氧阴离子对六价铬的还原几乎没有影响,而其他重金属的存在则有相对显著的影响。还分析了受六价铬影响的微生物群落结构和功能基因的进化行为,这为研究中生物还原的潜在机制提供了新的见解。这些结果对与铬有关的细菌种类和基因的还原机制有了新的认识,这有助于设计受六价铬污染水的生物修复策略。

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